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Large-flowered Skullcap Recovery Plan - U.S. Fish and Wildlife ...

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In Georgia, plants have been successfully transplanted from a site slated for development<br />

<strong>and</strong> have been relocated to two sites in the Chattahoochee National Forest (Woster,<br />

personal communication, 1993). The plants were collected while they were flowering <strong>and</strong><br />

were held by the Atlanta Botanical Garden over the winter. They were placed on slopes<br />

facing both east <strong>and</strong> west, where they have been monitored for two field seasons.<br />

<strong>Recovery</strong> Strategy<br />

Long-term monitoring ofScutellaria montana on protected l<strong>and</strong> is an important strategy<br />

for the recovery of the species. Monitoring should include permanent plots on areas with<br />

different management histories <strong>and</strong> forest compositions. By following individual plants<br />

<strong>and</strong> plots through several years, trends in recruitment, mortality, <strong>and</strong> reproductive<br />

capacity can be determined. With plots in a variety of forest types <strong>and</strong> management<br />

histories, the effects ofdisturbance <strong>and</strong> management activities on reproductive capacity<br />

can be followed.<br />

Life history studies, including studies ofpollination <strong>and</strong> germination requirements,<br />

phenology, <strong>and</strong> seed dispersal, could be a component ofa monitoring program.<br />

Determination ofgermination requirements will require laboratory studies.<br />

The Tennessee River Gorge, Hicks Gap, <strong>and</strong> Marshall Forest sites offer the greatest<br />

potential for gains in studying this species over a range ofconditions. Lookout Mountain<br />

would be another important site for study; it provides a fairly large <strong>and</strong> relatively<br />

undisturbed area, where monitoring would be useful.<br />

The protection of sizeable populations that occur on private l<strong>and</strong> is another important<br />

component ofthe recovery of Scutellaria montana. Currently, the second <strong>and</strong> third<br />

largest populations occur on private l<strong>and</strong>. These sites support populations considerably<br />

larger than several publicly owned <strong>and</strong> protected sites.<br />

A search for additional populations of Scutellaria montana throughout southeastern<br />

Tennessee, northwestern Georgia, <strong>and</strong> northeastern Alabama will also be conducted to try<br />

to increase the number ofknown extant populations.<br />

Management plans should be developed for public l<strong>and</strong> that is managed for recreation.<br />

The plans should include limiting access to areas ofhabitat for Scutellaria montana <strong>and</strong><br />

the removal ofinvasive plant species that threaten populations on those sites. Additional<br />

management needs should be incorporated into the management plans as the needs are<br />

identified.<br />

Propagation methods should be tested, <strong>and</strong> seeds should be placed in long-term storage.<br />

Propagation from cuttings has shown some success <strong>and</strong> should be investigated further<br />

(Patrick, Georgia Department of Natural Resources, Freshwater Wetl<strong>and</strong>s Heritage<br />

Inventory, personal communication, 1993).<br />

10

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